Fast Degradation of Azo Dyes by Using Cu-based Metallic Glasses
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Advances in Materials 2021; 10(1): 1-4 http://www.sciencepublishinggroup.com/j/am doi: 10.11648/j.am.20211001.11 ISSN: 2327-2503 (Print); ISSN: 2327-252X (Online) Fast Degradation of Azo Dyes by Using Cu-based Metallic Glasses Xiao Chen Xu1, 2, Ke Qiang Qiu1, * 1 Material Science and Engineering College, Shenyang University of Technology, Shenyang, China 2 Mechanical and Power Engineering College, Yingkou Institute of Technology, Yingkou, China Email address: * Corresponding author To cite this article: Xiao Chen Xu, Ke Qiang Qiu. Fast Degradation of Azo Dyes by Using Cu-based Metallic Glasses. Advances in Materials. Vol. 10, No. 1, 2021, pp. 1-4. doi: 10.11648/j.am.20211001.11 Received: January 11, 2021; Accepted: January 20, 2021; Published: January 28, 2021 Abstract: Wastewater containing azo dye has become a main harm in water pollution. Therefore, development of environment friendly materials with efficient purifying capacity seized more and more attention of people devoting to dye wastewater processing. On the other hand, advancement of metallic glasses in degrading organic water contaminant has also received wide concern. Cu-based amorphous alloy has excellent corrosion resistance and good stability in the process of degradation of azo dyes In the present thesis, single roller melt-spinning method Cu-Zr-Al-Y metallic glasses is applied so as to investigate degradation of azo dye Direct Blue in acid and alkaline solution. It is concluded that when the value of it is 2, 25µm ~ 30µm thick stripes of non-crystalline structures will be formed. With variation of the pH, rate of degradation will also change. The degradation rate in acidic solution is higher than that in alkaline and neutral solution. This is due to the fact that Azo bond and Cu-based amorphous alloy in dye molecule requires quite low activation energy to react, which makes degradation easier to proceed and thus macroscopic decoloration is also quickened. After the treatment of wastewater, white corrosion products will be produced on the surface of amorphous strip. It will affect the degradation effect. Keywords: Cu-based Metallic Glasses, Direct Blue Azo Dye, Degradation 1. Introduction In the last few years, the discharge of industrial wastewater, could degrade the azo dye of acid orange II dye solution [9, especially printing and dyeing wastewater, has caused great 10], and degrading effect of it is better than harm to the natural environment and people's living water, so homo-componential crystalline alloy and commercial iron treatment of wastewater has become urgent. At present, there powder Wang [11] produced Mg-Zn-Ca powder through are many methods to degrade dye wastewater, such as, ball-milling method, and it turns out that Mg-Zn-Ca powder Activated carbon adsorption method, chemical oxidation bears stronger degrading and decay resistance properties than method, and biodegradation method. However, it is necessary its corresponding crystalline-state powder. Amorphous-state to find a method that is efficient, cost-effective and Mg-Zn-Ca powder also shows a superior reacting efficiency in environmental friendly to solve the problem, from the degrading the Congo Red dye [12]. standpoints of both resource conservation and environmental We studied the reactivity of Cu-Zr-Al-Y metallic glasses in remediation. Therefore, besides its application value in degrading Direct Blue azo dye solutions. The influence of pH, mechanics, magnetic property, decay resistance etc, reaction temperature, and dosage has been studied. The non-crystalline material is also known as a functional material, reaction mechanism has been studied based on the evolution and can be used as catalyzer [1, 2], biological material [3, 4], of surface morphologies and the compositions change for the Soft magnetic material [5, 6] and in magneto caloric effect [7, metallic glass ribbons. 8]. It is recently discovered that, Fe—Si—B amorphous alloy
2 Xiao Chen Xu and Ke Qiang Qiu: Fast Degradation of Azo Dyes by Using Cu-based Metallic Glasses 2. Experimental 3. Results and Discussion 2.1. Reactivity Measurements 3.1. Characterization of the Cu46Zr45Al7Y2 Catalyst All experiments were conducted in 100mL beakers, which Figure 1 shows the XRD patterns of Cu46Zr45Al7Y2 were placed in a magnetic stirrer. During the reaction, the metallic glass ribbonss. It can be seen from the figure that the solution was rod-stirred at a xed speed. At present time intervals, alloy strip is completely amorphous, and there are two obvious 3 mL aliquots were removed with a syringe and altered with diffuse reflection peaks at the interval of 30-50° and 60-75°, 0.45 mm membranes [13]. The altered samples were pipetted which is the typical structure of amorphous alloy. out and subjected to UV-vis spectrum scanning. The reacted amorphous alloy strips were recycled and used for the degradation of dye wastewater again to test the reusability of amorphous alloy in the degradation of dye wastewater. The mass of amorphous alloy strips used in each experiment was 1.0 g, the volume of was 30mL, the initial concentration of Direct Blue solution was 0.1g/L, and the solution temperature was kept at 40°C in the degradation experiment, and the experimental parameters remained unchanged unless specified. The acidity of the solutions was tuned by adding 1 M HCL solution or 1M NaOH solution. For each time, 30 mL Direct Dlue solution was put into the 100 mL beaker for reaction test. The temperature was controlled by magnetic stirrer. 2.2. Fabrication and Characterization The alloy ingots with nominal compositions of Cu46Zr45Al7Y2 were prepared by induction melting the Figure 1. XRD patterns of Cu46Zr45Al7Y2 amorphous ribbons. mix-tures of pure Cu, Zr, Al, Ymetals under high purity argon 3.2. The Reactivity in Solutions with Different pH atmosphere. The Cu46Zr45Al7Y2 metallic glass ribbons were fabricated by single roller melt-spinning method under the Figure 2 shows the effect of pH value on degradation protection of argon atmosphere [14]. The atomic structure of efficiency from azo dyes by using Cu-Based amorphous alloys. the ribbons was verifified by X-ray diffraction. The pH of the solution plays an important role in the degradation of the dye. A slight change in pH will alter the 2.3. Mechanism Analysis degradation of the dye by the material. For most dye The morphology and structure of the ribbons before and wastewater, the pH is in the range of 2–10. In this work, after degradation were examined by scanning electron therefore, we chose to degrade the Direct Blue at pH = 2, 7 and microscopy (SEM) and XRD. The surface compositions of 10. Figure 2(a) shows the UV absorption spectra of Direct ribbons was also examined by energy dispersive spectroscopy Blue 6 dye by using Cu46Zr45Al7Y2 amorphous ribbons. It can (EDS) equipped on the SEM machine. [14] UV-vis spectra of indicate that the dye is completely degraded. The azo dye solutions were recorded using an UV-vis characteristic absorption peak of Direct Dlue dye molecules spectrometer. arises from 573 nm. Figure 2. UV-visible absorption spectrum of the Drect Blue solution of the Cu46Zr45Al7Y2amorphous alloy strip at (a) pH=2, (b) pH=7and, (c) pH=10 trestedatdifferent treatingtime In acidic conditions, the UV-visible absorption spectrum of that under acidic conditions, as the reaction time prolongs, the the Drect Blue 6 solution of the Cu46Zr45Al7Y2 amorphous intensity of the absorption peak at 573 nm decreases alloy strip degradation is shown in Figure 2 (a). It can be seen continuously, indicating that the -N=N- structure of the direct
Advances in Materials 2021; 10(1): 1-4 3 blue dye molecule is continuously destroyed until it is almost surface of the positively charged cu-based amorphous alloy, completely decomposed. In acidic conditions, the Direct Dlue and as the pH of the solution increases, the positive charge is dye can be completely degraded in 25 min with high reduced, the adsorption becomes more and more difficult, and degradation efficiency. At pH=7, the UV-visible absorption the rate of subsequent degradation reaction is further slowed spectrum of the Direct Dlue solution of the Cu46Zr45Al7Y2 down. amorphous alloy strip degradation is shown in Figure 2(b). For every 10 minutes increase, the intensity of the absorption 3.3. The Analysis of Surface Morphology peak at 573 nm is less and less, which indicates that the In order to clarity the surface morphology of glassy ribbon degradation rate of Direct Dlue is slower and slower, after cycle use on the degradation efficiency of simulated especially when the reaction proceeds to 40 min, the change in images of glassy ribbons before degradation. As shown in absorption peak intensity has been very weak at 573 nm. Figure 3(a) the surface of the amorphous strip is smooth Figure 2(c) shows that in alkaline conditions, the Direct Dlue without cracks before degradation. Figure (b), (c) and (d) degradation of becomes more difficult. This is because the show that there are white corrosion products on the surface of Direct Blue solution is negatively charged in the acidic amorphous alloy after wastewater degradation [15]. solution, so when the p H is low, it is easily adsorbed on the Figure 3. SEM images of Cu46Zr45Al7Y2 glassy ribbon before degradation (a) and after the first cycle (b) and two cycles (c) and five cycles of use (d). So far, many researchers have used different amorphous Liaoning Province (Grant No. 2019ZD0373). alloys to treat various kinds of wastewater. As shown in Table 1, the comparison of research results shows that Cu-based amorphous alloy has outstanding advantages. References Table 1. Comparison of azo dyes treated with different amorphous alloys. [1] Carmo M, Sekol R. C, Ding S. Y. Bulk metallic glass nanowire architecture for electrochemical applications [J]. ACS Nano, Pollutants Material Time References 2011, 5: 2979-2983. Direct blue2B Al-Ni-Y 120min [14] Direct blue6 Fe-Si-B 60min [13] [2] Tang Y, Chen N, et al. Insight into the high reactivity of Direct blue6 Fe-B 60min [16] commercial Fe-Si-B amorphous zero-valent iron in degrading Direct blue6 Cu-Zr-Al-Y 25min Tihis work azo dye solutions [J]. RSC Adv, 2015, 34032-34039. [3] Zberg B, Uggowitzer P J et al. Mg-Zn-Ca glasses without 4. Conclusions clinically observable hydrogen evolution for biodegradable implants [J]. Nat Mater, 2009, 887-891. Cu-based amorphous alloy has excellent corrosion resistance, so it has less corrosion loss in the process of [4] Schroers J, Kumar G et al. Bulk metallic glasses for biomedical applications [J]. JOM, 2009, 61: 21-29. degradation of azo dyes and can maintain its own stability. 1) The optimal processing parameters are included the pH [5] Egami T. Magnetic amorphous alloys: physical and value of 2, under the optimal parameters, the removal rates can technological applications [J]. Rep Prog Phys, 1984, 47: reach up to 98% respectively. This is because the Direct Blue 1601-1725. solution is negatively charged in the acidic solution, so when [6] Zhang M X, Kong F L, et al. Soft magnetic properties of bulk the p H is low, it is easily adsorbed on the surface of the Fe-C-Mo-P-C-B-Si glassy core prepared by copper mold positively charged cu-based amorphous alloy, and as the pH casting [J]. Appl Phys, 2012, 111 (07): 312. of the solution increases, the positive charge is reduced, the [7] Wang W H, Bulk metallic glasses with functional physical adsorption becomes more and more difficult properties [J]. Adv Mater. 2009, 21: 4524-4544. 2) Cu46Zr45Al7Y2 glassy ribbon possesses a good structural stability and excellent surface activity. [8] Huo J T, Huo L S et al. The magnetocaloric effect of Gd-Tb-Dy-Al-M (M Fe, Co and Ni) highentropy bulk metallic glasses [J]. Intermetallics, 2015, 58: 31-35. Acknowledgements [9] Zhang] C. Q., Zhang H. F., et al, Decolorization of azo dye This work was supported by Natural Science Foundation of solution by Fe-Mo-Si-B amorphous alloy [J]. J. Non Cryst. Solids, 2010, 356: 1703-1706.
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